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EC number: 413-550-5 | CAS number: 142068-96-0 H112339
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Toxicity to microorganisms
Administrative data
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 31 October 1991 to 12 December 1991
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted in compliance with GLP to available methods at the time. Effects are well documented.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 992
- Report date:
- 1992
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- other: ETAD - Ecological Method No 103
- Deviations:
- not applicable
- Qualifier:
- according to guideline
- Guideline:
- other: Department of the Environment, UK (1977). Amenability of sewage sludge to anaerobic digestion
- Deviations:
- not applicable
- Principles of method if other than guideline:
- A number of different procedures were used for this work with the overall objectives of assessing potential adverse effects on aerobic and anaerobic sewage treatment processes and the likely degree of bioelimination of Substance HI 12339 in anaerobic processes. The following principles were adopted:
ETAD (Ecological and Toxicological Association of the Dyestuffs Manufacturing Industry). Ecological Method No 103 - A screening test for the Assessment of the Possible Inhibitory Effect of a Chemical Substance on Aerobic Waste-Water Bacteria.
(Note: This ETAD method formed the basis of the OECD Guideline 209 -Activated Sludge, Respiration Inhibition Test).
Department of the Environment, UK (1977). Amenability of sewage sludge to anaerobic digestion. HMSO London - GLP compliance:
- yes
Test material
- Reference substance name:
- Octasodium 2-(8-(4-chloro-6-(3-((4-chloro-6-(3,6-disulfonato-2-(1,5-disulfonatonaphthalen-2-ylazo)-1-hydroxynaphthalen-8-ylamino)-1,3,5-triazin-2-yl)aminomethyl)phenylamino)-1,3,5-triazin-2-ylamino)-3,6-disulfonato-1-hydroxynaphthalen-2-ylazo)naphthalene-1,5-disulfonate
- EC Number:
- 413-550-5
- EC Name:
- Octasodium 2-(8-(4-chloro-6-(3-((4-chloro-6-(3,6-disulfonato-2-(1,5-disulfonatonaphthalen-2-ylazo)-1-hydroxynaphthalen-8-ylamino)-1,3,5-triazin-2-yl)aminomethyl)phenylamino)-1,3,5-triazin-2-ylamino)-3,6-disulfonato-1-hydroxynaphthalen-2-ylazo)naphthalene-1,5-disulfonate
- Cas Number:
- 142068-96-0
- Molecular formula:
- Hill formula: C53H28Cl2N14Na8O26S8
- IUPAC Name:
- octasodium 5-[(4-chloro-6-{[4-({[4-chloro-6-({7-[2-(1,5-disulfonatonaphthalen-2-yl)diazen-1-yl]-8-hydroxy-3,6-disulfonatonaphthalen-1-yl}amino)-1,3,5-triazin-2-yl]amino}methyl)phenyl]amino}-1,3,5-triazin-2-yl)amino]-3-[2-(1,5-disulfonatonaphthalen-2-yl)diazen-1-yl]-4-hydroxynaphthalene-2,7-disulfonate
- Details on test material:
- - Name of test material (as cited in study report): V723
- Physical state: Dark brown powder
- Lot/batch No.: NBY 405/74
- Storage condition of test material: darkness at ambient temperature
Constituent 1
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
Not applicable.
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 28, 56 & 112 mg/l
Details on sampling are detailed below in "Details on Test Conditions".
Test solutions
- Vehicle:
- no
- Details on test solutions:
- See below under "Details on Test Conditions"
Test organisms
- Test organisms (species):
- other: aerobic and anaerobic sludge.
- Details on inoculum:
- Not specified within the report.
Study design
- Test type:
- other: aerobic and anaerobic
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 3 h
- Post exposure observation period:
- No post exposure observation
Test conditions
- Hardness:
- No data
- Test temperature:
- Variable, dependant on method used. See below under "details on test conditions".
- pH:
- No data
- Dissolved oxygen:
- No data
- Salinity:
- Not applicable.
- Nominal and measured concentrations:
- - Concentrations: 28, 56 & 112 mg/l (nominal)
- Details on test conditions:
- 4.1 Effect on respiration rate of activated sludge (Study V723/E)
The method used was that defined by the Ecological and Toxicological Association of Dyestuff Manufacturers (ETAD) as Ecological Method 103.
In outline the method consists of aerating a sample of activated sludge for 3 hr in the presence of the test substance and a synthetic sewage, and comparing its respiration rate after this period with that of the same activated sludge aerated for 3 hr in the presence of the synthetic sewage alone.
4.2 Effect on the nitrifying ability of activated sludge (Study V723/D)
The method used was that described by the UK Department of the Environment and measures any adverse effects on the nitrification process in activated sludge.
The experimental procedure involves incubating nitrifying sludge under aerobic conditions for a period of 4 hr in an inorganic medium containing ammonium ion. After this period the concentration of oxidised nitrogen formed in the presence of the test substance at a range of concentrations is compared with controls.
4.3 Effect on sludge digestion and determination of colour removal under anaerobic conditions (Study V723/F)
4.3.1 General description of procedure
The method assesses possible inhibition of anaerobic digestion by measuring the volume of gas produced in the presence and absence of the test substance.
The procedure used was a modification of the Department of the Environment UK method which is currently being amended for testing pure compounds and formulations. The general principles of the modified approach have been described by Owen et al.
For this test, samples of raw feed sludge and sludge from a heated digester were collected from a local sewage treatment works and, after sieving to remove gross particles, the dry sludge solids were determined.
Dry solids (% w/w)
Raw sludge 2.03
Digester sludge 1.03
The two sludges were mixed in the ratio of 1 part raw sludge :3 parts digester sludge. The pH of the raw sludge was adjusted to 7.6 with 2N NaOH and the pH of the mixture was found to be 7.1. The dry solids of the mixture was calculated as 1.28% w/w from the results obtained on the two component sludges.
The mixed sludge was then placed in the incubation bottles of batch digestion units with various amounts of V723 according to the experimental design shown in Table 2.
The incubation bottles were swirled to mix the contents and then allowed to stand for approximately 30 min at 35°C before connection to the gas measuring devices. Each day for the 15 days of the experiment the volume of gas collected was recorded and the results are summarised in Table 3. The temperature of the water bath was also recorded daily and was in the range 33 - 34°C.
4.4 Determination of colour removal
On the day on which the digestion inhibition test ended a sample of the supernatants from each of the test units was taken and analysed by the procedure detailed above. - Reference substance (positive control):
- yes
- Remarks:
- See above under "Details on Test Conditions"
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 3 h
- Dose descriptor:
- IC50
- Effect conc.:
- >= 100 mg/L
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 100 mg/L
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Details on results:
- Aerobic sewage treatment
(a) Substance HI 12339 at a nominal test level of 100 mg/1 caused a 2% inhibition of the respiration rate of an activated sludge as determined by the ETAD Method 103 . This inhibition is not considered to be significant and it is unlikely that Substance HI 12339 will affect aerobic sewage treatment.
(b) Substance HI 12339 at a test level of 100 mg/1 caused no inhibition of the nitrifying ability of activated sludge when measured by the standard Department of the Environment (UK) Method (Ref 2). It is unlikely that Substance HI 12339 will affect nitrification during sewage treatment.
Anaerobic sewage treatment
A batch anaerobic digestion experiment was carried out at levels of Substance HI 12339 of up to 4.4% w/w dry sludge solids. No significant inhibition of gas production was observed and it is considered unlikely that Substance HI 12339 will interfere with the sludge digestion process.
Colorimetric analysis of the supernatant at the end of the digestion experiment showed a mean colour removal of 98%. - Results with reference substance (positive control):
- 4.1 Effect on respiration rate of activated sludge (Study V723/E)
The results are summarised in Table 1 and show 2% inhibition of respiration at V723 test concentrations of 112 mg/I, 56 mg/1 and 28 mg/1. This is not considered to be significant.
The IC50 (concentration for 50% inhibition) of 3,5-dichlorophenol determined on the same batch of activated sludge was 8 mg/1 which is within the normal range (5-20 mg/1) suggested in the ETAD method for this substance.
4.2 Effect on the nitrifying ability of activated sludge (Study V723/D)
NO2 + NO3 formed at 4 hr inhibition (N - mg/I) (%)
Control (triplicate) 19.9
V723: 112 mg/1 (triplicate) 21.2 0
Allylthiourea (11.6 mg/1), used as a standard nitrification inhibitor, gave complete inhibition of nitrification in the same study. - Reported statistics and error estimates:
- Not reported.
Any other information on results incl. tables
TABLE 1 - STUDY V723/E: EFFECTS ON RESPIRATION RATE OF ACTIVATED SLUDGE
Test unit |
|
Mean respiration rate (mgO2/l/hr) |
% inhibition |
1,2,14,15 |
Controls |
51.5 |
- |
8,9 |
112 mg/1 V723 |
50.5 |
2 |
10,11 |
56 mg/1 V723 |
50.5 |
2 |
12,13 |
28 mg/1 V723 |
50.5 |
2 |
TABLE 2 - STUDY V723/F: EXPERIMENTAL DESIGN - ANAEROBIC SLUDGE DIGESTION
Test unit |
|
Sludge volume (ml) |
V723 (mg)1 |
Total volume (ml) |
1,2,21,22 |
Controls |
300 |
- |
400 |
15,16 |
V723 (4.9% on dry solids) |
300 |
189 |
400 |
17,18 |
V723 (2.5% on dry solids) |
300 |
95 |
400 |
19,20 |
V723 (0.89% on dry solids) |
300 |
34 |
400 |
NOTE
1 The V723 was added by adding the appropriate volume of a 2500 mg/1 standard solution of V723 in water.
TABLE 3 - STUDY V723/F: EFFECTS ON ANAEROBIC SLUDGE DIGESTION
|
|
Mean Cumulated gas production (ml) at various time intervals (days) |
||||
Test Unit |
|
1 |
3 |
5 |
10 |
15 |
1,2,21,22 |
Controls |
70 |
326 |
421 |
523 |
563 |
15,16 |
V723 (4.9% on dry solids) |
61 |
297 |
387 |
484 |
523 |
15,16 |
Inhibition |
13% |
9% |
8% |
8% |
7% |
17,18 |
V723 (2.5% on dry solids) |
62 |
310 |
403 |
501 |
540 |
17,18 |
Inhibition |
11% |
5% |
4% |
4% |
4% |
19,20 |
V723 (0.89% on dry solids) |
65 |
318 |
413 |
513 |
552 |
19,20 |
Inhibition |
7% |
3% |
2% |
2% |
2% |
TABLE 4 – STUDY V723/F: DECOLOURISATION – ANAEROBIC SLUDGE DIGESTION
Test |
|
Initial concn |
Measured concn |
% |
unit |
|
of V723 (mg/1) |
of V723 after 15 days |
Decolour- |
|
|
|
digestion (mg/1) |
isation |
15 |
V723 (4.9% on dry |
473 |
8.2 |
98 |
16 |
solids) |
473 |
8.0 |
98 |
17 |
V723 (2.5% on dry |
238 |
4.4 |
98 |
18 |
solids) |
238 |
4.3 |
98 |
19 |
V723 (0.89% on dry |
85 |
1.2 |
99 |
20 |
solids) |
85 |
2.4 |
97 |
Mean decolourisation: 98%
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- Substance HI 12339 at a nominal test level of 100 mg/1 caused a 2% inhibition of the respiration rate of an activated sludge as determined by the ETAD Method 103 (Ref 1). This inhibition is not considered to be significant and it is unlikely that Substance HI 12339 will affect aerobic sewage treatment
Substance HI 12339 at a test level of 100 mg/1 caused no inhibition of the nitrifying ability of activated sludge when measured by the standard Department of the Environment (UK) Method (Ref 2). It is unlikely that Substance HI 12339 will affect nitrification during sewage treatment.
The results show 2% inhibition of respiration at V723 test concentrations of 112 mg/I, 56 mg/1 and 28 mg/1. This is not considered to be significant.
The IC50 (concentration for 50% inhibition) of 3,5-dichlorophenol determined on the same batch of activated sludge was 8 mg/1 which is within the normal range (5-20 mg/1) suggested in the ETAD method for this substance - Executive summary:
Study conducted in compliance with GLP and to the following test procedures
1 ETAD (Ecological and Toxicological Association of the Dyestuffs Manufacturing Industry). Ecological Method No 103 - A screening test for the Assessment of the Possible Inhibitory Effect of a Chemical Substance on Aerobic Waste-Water Bacteria.
(Note: This ETAD method formed the basis of the OECD Guideline 209 -Activated Sludge, Respiration Inhibition Test).
2 Department of the Environment, UK (1977). Amenability of sewage sludge to anaerobic digestion. HMSO London
No effects were noticed that were due to the test substance. The substance is not considered to inhibit the respiration or nitrification of sewage sludge microorganisms. EC50 > 100mg/l
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